Secondary organic aerosol formation and primary organic aerosol oxidation from biomass-burning smoke in a flow reactor during FLAME-3
We report the physical and chemical effects of photochemically aging dilute biomass-burning smoke. A "potential aerosol mass" (PAM) flow reactor was used with analysis by a high-resolution aerosol mass spectrometer and a proton-transfer-reaction ion-trap mass spectrometer during the FLAME-...
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2013-11-01
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doaj-335b707fde5a4dae8c3b75d2204770aa2020-11-25T01:23:43ZengCopernicus PublicationsAtmospheric Chemistry and Physics1680-73161680-73242013-11-011322115511157110.5194/acp-13-11551-2013Secondary organic aerosol formation and primary organic aerosol oxidation from biomass-burning smoke in a flow reactor during FLAME-3A. M. Ortega0D. A. Day1M. J. Cubison2W. H. Brune3D. Bon4J. A. de Gouw5J. L. Jimenez6Cooperative Institute for Research in the Environmental Sciences, University of Colorado, Boulder, CO, USACooperative Institute for Research in the Environmental Sciences, University of Colorado, Boulder, CO, USACooperative Institute for Research in the Environmental Sciences, University of Colorado, Boulder, CO, USADepartment of Meteorology, Pennsylvania State University, University Park, PA, USACooperative Institute for Research in the Environmental Sciences, University of Colorado, Boulder, CO, USACooperative Institute for Research in the Environmental Sciences, University of Colorado, Boulder, CO, USACooperative Institute for Research in the Environmental Sciences, University of Colorado, Boulder, CO, USAWe report the physical and chemical effects of photochemically aging dilute biomass-burning smoke. A "potential aerosol mass" (PAM) flow reactor was used with analysis by a high-resolution aerosol mass spectrometer and a proton-transfer-reaction ion-trap mass spectrometer during the FLAME-3 campaign. Hydroxyl (OH) radical concentrations in the reactor reached up to ~1000 times average tropospheric levels, producing effective OH exposures equivalent to up to 5 days of aging in the atmosphere, and allowing for us to extend the investigation of smoke aging beyond the oxidation levels achieved in traditional smog chambers. Volatile organic compound (VOC) observations show aromatics and terpenes decrease with aging, while formic acid and other unidentified oxidation products increase. Unidentified gas-phase oxidation products, previously observed in atmospheric and laboratory measurements, were observed here, including evidence of multiple generations of photochemistry. Substantial new organic aerosol (OA) mass ("net SOA"; secondary OA) was observed from aging biomass-burning smoke, resulting in total OA average of 1.42 ± 0.36 times the initial primary OA (POA) after oxidation. This study confirms that the net-SOA-to-POA ratio of biomass-burning smoke is far lower on average than that observed for urban emissions. Although most fuels were very reproducible, significant differences were observed among the biomasses, with some fuels resulting in a doubling of the OA mass, while for others a very small increase or even a decrease was observed. Net SOA formation in the photochemical reactor increased with OH exposure (OH<sub>exp</sub>), typically peaking around three days of equivalent atmospheric photochemical age (OH<sub>exp</sub>~3.9 × 10<sup>11</sup> molecules cm<sup>−3</sup> s), then leveling off at higher exposures. The amount of additional OA mass added from aging is positively correlated with initial POA concentration, but not with the total VOC concentration or the concentration of known SOA precursors. The mass of SOA formed often exceeded the mass of the known VOC precursors, indicating the likely importance of primary semivolatile/intermediate volatility species, and possibly of unidentified VOCs as SOA precursors in biomass burning smoke. Chemical transformations continued even after mass concentration stabilized. Changes in the biomass-burning tracer <i>f</i><sub>60</sub> ranged from substantially decreasing to remaining constant with increased aging. With increased OH<sub>exp</sub>, oxidation was always detected (as indicated by <i>f</i><sub>44</sub> and O/C). POA O/C ranged from 0.15 to 0.5, while aged OA O/C reached up to 0.87. The rate of oxidation and maximum O/C achieved differs for each biomass, and appears to increase with the initial O/C of the POA.http://www.atmos-chem-phys.net/13/11551/2013/acp-13-11551-2013.pdf |
collection |
DOAJ |
language |
English |
format |
Article |
sources |
DOAJ |
author |
A. M. Ortega D. A. Day M. J. Cubison W. H. Brune D. Bon J. A. de Gouw J. L. Jimenez |
spellingShingle |
A. M. Ortega D. A. Day M. J. Cubison W. H. Brune D. Bon J. A. de Gouw J. L. Jimenez Secondary organic aerosol formation and primary organic aerosol oxidation from biomass-burning smoke in a flow reactor during FLAME-3 Atmospheric Chemistry and Physics |
author_facet |
A. M. Ortega D. A. Day M. J. Cubison W. H. Brune D. Bon J. A. de Gouw J. L. Jimenez |
author_sort |
A. M. Ortega |
title |
Secondary organic aerosol formation and primary organic aerosol oxidation from biomass-burning smoke in a flow reactor during FLAME-3 |
title_short |
Secondary organic aerosol formation and primary organic aerosol oxidation from biomass-burning smoke in a flow reactor during FLAME-3 |
title_full |
Secondary organic aerosol formation and primary organic aerosol oxidation from biomass-burning smoke in a flow reactor during FLAME-3 |
title_fullStr |
Secondary organic aerosol formation and primary organic aerosol oxidation from biomass-burning smoke in a flow reactor during FLAME-3 |
title_full_unstemmed |
Secondary organic aerosol formation and primary organic aerosol oxidation from biomass-burning smoke in a flow reactor during FLAME-3 |
title_sort |
secondary organic aerosol formation and primary organic aerosol oxidation from biomass-burning smoke in a flow reactor during flame-3 |
publisher |
Copernicus Publications |
series |
Atmospheric Chemistry and Physics |
issn |
1680-7316 1680-7324 |
publishDate |
2013-11-01 |
description |
We report the physical and chemical effects of
photochemically aging dilute biomass-burning smoke. A "potential aerosol
mass" (PAM) flow reactor was used with analysis by a high-resolution aerosol
mass spectrometer and a proton-transfer-reaction ion-trap mass spectrometer
during the FLAME-3 campaign. Hydroxyl (OH) radical concentrations in the
reactor reached up to ~1000 times average tropospheric
levels, producing effective OH exposures equivalent to up to 5 days of aging in
the atmosphere, and allowing for us to extend the investigation of smoke aging
beyond the oxidation levels achieved in traditional smog chambers. Volatile organic
compound (VOC) observations show aromatics and terpenes decrease with aging, while formic
acid and other unidentified oxidation products increase. Unidentified
gas-phase oxidation products, previously observed in atmospheric and
laboratory measurements, were observed here, including evidence of multiple
generations of photochemistry. Substantial new organic aerosol (OA) mass
("net SOA"; secondary OA) was observed from aging biomass-burning smoke,
resulting in total OA average of 1.42 ± 0.36 times the initial primary
OA (POA) after oxidation. This study confirms that the net-SOA-to-POA ratio
of biomass-burning smoke is far lower on average than that observed for
urban emissions. Although most fuels were very reproducible, significant
differences were observed among the biomasses, with some fuels resulting in
a doubling of the OA mass, while for others a very small increase or even a
decrease was observed. Net SOA formation in the photochemical reactor
increased with OH exposure (OH<sub>exp</sub>), typically peaking around three days
of equivalent atmospheric photochemical age (OH<sub>exp</sub>~3.9 × 10<sup>11</sup> molecules cm<sup>−3</sup> s), then leveling off at higher
exposures. The amount of additional OA mass added from aging is positively
correlated with initial POA concentration, but not with the total VOC
concentration or the concentration of known SOA precursors. The mass of SOA formed often exceeded the mass of
the known VOC precursors, indicating the likely importance of primary
semivolatile/intermediate volatility species, and possibly of
unidentified VOCs as SOA precursors in biomass burning smoke. Chemical transformations continued even after mass concentration stabilized. Changes in the biomass-burning tracer <i>f</i><sub>60</sub> ranged from
substantially decreasing to remaining constant with increased aging. With
increased OH<sub>exp</sub>, oxidation was always detected (as indicated by
<i>f</i><sub>44</sub> and O/C). POA O/C ranged from 0.15 to 0.5, while aged OA O/C reached up to
0.87. The rate of oxidation and maximum O/C achieved differs for each
biomass, and appears to increase with the initial O/C of the POA. |
url |
http://www.atmos-chem-phys.net/13/11551/2013/acp-13-11551-2013.pdf |
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